Waste Minimization and Cleaner Production

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    Waste Minimization and

    Cleaner Production

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    Introduction In the last 15 20 years there has been a growing world

    wide movement among government and industry to changethe way industry interacts with the environment.

    The focus of this movement has been to reduceenvironmental impacts from industry through changes inindustrial behavior and technology.

    All of them are based on what is commonly known as theprecautionary Principle, also known by the old saying,

    An ounce of prevention is worth a pound of cure.

    It is better, and usually much less expensive, to preventenvironmental problems from happening than to fix themonce they are created.

    And if we dont know what effects our actions will have onthe environment, we should proceed with caution and try tominimize any potential effects that might occur.

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    Objective

    The objective of this lecture is to briefly define the mostcommon concepts used for industrial environmentalmanagement and to show their relationships.

    There are many actions industry can take, from the

    small to the very large, along a path orstaircase thatleads to increasingly broad impacts on and interactionswith the environment and society.

    No industry, and no society, is really at the top of thestaircase; the top, which is sustainable development, is,like quality, a goal which is always elusive and for whichwe should never stop striving.

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    The Staircase of Concepts In IndustrialEnvironmental Management

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    Concept of Stair Case

    There are three types of concepts on the staircase.

    (1)Macro-scale concepts:

    The macro-scale concepts ofsustainable development and industrialecology extend far beyond the firm and include relationships betweencompanies, social institutions, the public and the environment in all its facets.

    (2) Firm-wide concepts:

    The firm-wide concepts of environmental management systems and cleanerproductionaddress all aspects of the firms operations, from use of naturalresources to suppliers to production to product use to product disposal.

    (3) Operational concepts:

    The remaining operational concepts address specific functions of the

    business.

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    Macro-Scale Concepts

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    Sustainable Development

    Sustainable development is the development that meets the

    needs of the present without compromising the ability of futuregenerations to meet their own needs

    It contains within it two key concepts:

    The concept of "needs", in particular the essential needs of the world's poor, towhich overriding priority should be given; and

    The idea oflimitations imposed by the state of technology and social organizationon the environment's ability to meet present and future needs.

    Thus the goals ofeconomic and social development must be defined in terms ofsustainability in all countries -- developed or developing, market-oriented or centrally

    planned.

    Interpretations will vary, but must share certain general features and must flow from a

    consensus on the basic concept of sustainable development and on a broadstrategic framework for achieving it.

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    Industrial Ecology

    Industrial ecology is the means by which humanity candeliberately and rationally approach and maintain adesirable carrying capacity, given continued economic,cultural and technological evolution.

    The concept requires that an industrial system be viewednot in isolation from its surrounding systems, but in concertwith them.

    It is a system view in which one seeks to optimize the totalmaterials cycle from virgin material, to finished material, toproduct, to waste product, and to ultimate disposal.

    Factors to be optimized include resources, energy and

    capital

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    Aim of Industrial Ecology

    The aim of industrial ecology is to interpret andadapt an understanding of the natural systemand apply it to the design of the man-madesystem, in order to achieve a pattern ofindustrialization that is not only more efficient,but that is intrinsically adjusted to the tolerancesand characteristics of the natural system.

    The emphasis is on forms of technology that workwithnatural systems, not againstthem...

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    Firm-Wide Concepts

    These are concepts that affect the whole scope of the business enterprise, not just

    parts of it.

    They are essentially management philosophies and practices rather than technical

    practices and as such are best directed to the top levels of management.

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    Cleaner Production

    Cleaner production means the continuous application of an integratedpreventive environmental strategy to processes and products to reduce risks

    to humans and the environment.

    For production processes, cleaner production includes conserving raw materials

    and energy, eliminating toxic raw materials, and reducing the quantity and toxicity of

    all emissions and wastes before they leave a process.

    For products, the strategy focuses on reducing impacts along the entire life cycleof the product, from raw material extraction to the ultimate disposal of the product.

    Cleaner production is achieved by applying know-how, by improving technology,

    and by changing attitudes.

    The conceptual and procedural approach to production that demands that all

    phases of the life-cycle of products must be addressed with the objective of the

    prevention or minimization of short and long-term risks to humans and the

    environment.

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    Pollution Prevention

    The USA Pollution Prevention Act of 1990 defines pollution prevention as a

    goal which is realized through source reduction.

    The term ''source reduction'' [or pollution prevention] means any practicewhich

    Reduces the amount of any hazardous substance, pollutant, orcontaminant entering any waste stream or otherwise released into the

    environment (including fugitive emissions) prior to recycling, treatment,or disposal

    Reduce the hazards to public health and the environment associated withthe release of such substances, pollutants, or contaminants

    The term includes equipment or technology modifications, process orprocedure modifications, reformulation or redesign of products,substitution of raw materials, and improvements in housekeeping,maintenance, training, or inventory control.

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    Operational Concepts

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    Why Waste Minimization ?

    The generation of large volumes of waste correlates with

    the depletion of mostly non-renewable resources

    The energy requirement for the transformation and

    upgrading of wastes is in proportion to the quantities treated

    and rises exponentially with increasing dilution of the waste

    The increasing total costs for collection, segregation,

    intermediate storage, transport etc.

    Increased public and legislative pressures seem likely to do

    mitigated only by waste reduction/minimization

    Since waste equals inefficiency, reducing waste increases

    efficiency and hence profitability

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    Waste Minimization

    Waste Minimization (WM) is the reduction, to the extent feasible, of hazardous

    waste that is generated or subsequently treated, sorted or disposed.

    It includes any source reduction or recycling activity undertaken by a generator

    that results in either

    (1) The reduction of total volume or quantity of hazardous waste, or

    (2) The reduction of toxicity of hazardous waste, or both, so long as such

    reduction is consistent with the goal of minimizing recent and future threats to

    human health and the environment.

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    Clean Technology

    It has two ideas

    1. The emphasis is on the generation of less waste and onthe consumption of fewer raw materials and less energy.Thus a simple but satisfactory definition of cleantechnology is any technology or process which uses

    fewer raw materials and/or less energy, and/or generatesless waste than an exiting technology or processes.

    2. The avoidance of end-of-pipe emission reduction is alsoemphasized. End-of-pipe methods are those that attemptsto reduce the environmental impact of a waste, after thatwaste has been produced.

    Th t f i i h b

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    The concept of zero emission processes has beenespoused, such a target is thermodynamically impossiblefor a manufacturing processes, if such processes isregarded as an open system (a system that exchangesboth material and energy with its surroundings).

    Manipulating the system boundary in an attempt toproduce a closed system (One that exchanges only

    energy and not materials with its surroundings) isanalogous to the end-of-pipe solutions to materialproblems, which merely transfers matter from onemedium to the other.

    Enlarging the systems boundary to incorporate theenergy supply facility reveals that the enlarged system isin fact, open and depositing material into thesurrounding.

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    What is life cycle assessment ?

    It is a systematic inventory and comprehensive assessment of environmental effectsof two or more alternative activities involving a defined product in a defined space

    and time including all steps and co-products in its life cycle.

    Any product may have following stages in its life cycle

    Raw materials acquisition

    Bulk material processing

    Engineered and specialty material production

    Manufacturing and assembly

    use and service

    Retirement Disposal

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    Product life cycle system (from Koelein and Menerey, 1993)

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    Steps Necessary to conduct a Life Cycle Assessment

    An LCA has the following phases:

    Planning Screening

    Data collection (inventory) Data treatment (aggregation/classification) Evaluation

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    (material down scaling into another product system)

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    West Reproduction Technique

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    Thermodynamics and Material Flows in the Economy

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    Transformationprocess

    Material inputs

    Energy inputs

    Wastes & emissions

    Useful outputs

    Thermodynamics and Material Flows in the Economy

    1. Law of Thermodynamics:Conservation of energy

    In non-nuclear processes energy can neither be created nor destroyed. Energy can onlybe transformed from one form into another. The total amount of energy input to a non-

    nuclear transformation process is thus equal to the total amount of energy output.

    Conservation of massThe total mass of material inputs into a (non-nuclear) material transformation process is

    equal to the total mass of material outputs.

    Conservation of mass per chemical elementThe total mass of each chemical element is conserved during every (non-nuclear)

    material transformation process.

    The material transformation process

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    afterbefore

    outputinput

    emissionswastesproductsancillarydirect

    EntropyEntropy

    EnergyEnergy

    MassMassMassMassMass

    Direct materials

    Ancillary materials

    Low-entropy energy

    Economic output

    Wastes & emissions

    High-entropy energy

    Transformation process

    1. Law of TD

    2. Law of TD

    e ate a t a s o at o p ocess

    Solar Radiation Earths RadiationMaterial Flows in the Economy

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    Ecosphere

    Anthroposphere

    Materials

    Sink for:

    Wastes

    &Emissions

    Needs & Wants

    (Teff~ 6000K

    mainly UV, optical and IR)(Teff~ 300K

    mainly IR)

    Services

    Products

    Production

    All materials that enter the economic system will eventually leave it

    Large amounts of low-entropy energy are needed to drive the economic system

    All economic activity is essentially dissipative in both materials and/or energy

    Low-entropyEnergy

    Material Flows in the Economy

    high-entropy

    Energy

    Material Flow Analysis (MFA)

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    Accounting methodology for material stocks:

    Producing

    processes

    Imports Exports

    Consuming

    processes

    Stocks of

    upstream

    materials

    Stocks of

    downstream

    materials

    Stocks outside

    of boundaries

    Stocks outside

    of boundaries

    Material

    stock

    Transformation processes

    Transportation processes

    lllll

    tt

    ExportImportnConsumptioProductionStock

    tdExportImportnConsumptioProductionStockdStock

    Methodology Single material or substance

    MFA Methodology Single material or substance

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    Material

    production

    Potential

    Waste

    Component

    fabrication

    Product

    Assembly

    Product

    Use

    Raw

    Material

    Material Components Products

    Imports / Exports

    Domestic Environment

    Extraction ReleaseRecycling Reuse

    Example: Copper Flows in North America in 1994 (in kt / y)

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    Import / Export

    EnvironmentLithosphere

    Production:

    Mill, Smelter,

    Refinery

    Fabrication &

    Manufacturing

    Use Waste

    Management

    Concentrate,

    Blister, Cathode

    325

    Ingots

    3

    Semis,

    Finished Products

    17

    Stock

    Cathode

    3270Prod. Cu

    2640

    Prod. Alloy

    690

    Stock

    1920

    Discards

    1410

    Old

    Scrap

    190

    New Scrap

    730140

    Old Scrap180330

    Tailings & Slag 365

    Ore

    3130

    Landfilled Waste,

    Dissipated

    Source: CIE, Yale

    710

    3

    Recycling

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    Recycling

    There are almost always some wastes created by production processes, so they

    need to be recycled as much as possible. Recycling can be broken down into

    closed-loop recycling (which is really just a production process extension rather

    than recycling), on-site recycling and re-use, off-site recycling, and reclamation.

    Common Effluent Treatment Plants

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    Leachate collection and ewaporation pond

    at the common facility for waste

    management at Hyderabad (A.P.)

    Common Effluent Treatment Plants

    Oxidation Pond based Treatment Plant

    at Vrindavan, UP

    Pollution Control

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    Pollution Control

    Pollution control systems to reduce waste volume or toxicity are a necessityto manage wastes that cannot be prevented or exchanged. The relationship

    to the higher concepts is one of fast resort

    Waste Disposal

    A view of hazardous waste storage pits

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    Indian Scenario

    Hazardous Wests Generating Units &

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    g

    HW Generation Scenario

    HW generation in States - No uniform trend No. of Units generating Hazardous Wastes gone-

    up

    Factors responsible:

    Changes in regulatory classification:o Change over from 18 waste categories with

    annual threshold limits to 36 processes and

    corresponding waste streams

    o Emphasis on waste minimization-zerodischarge(Tanneries,textiles)

    o Fly-ash,gypsum sludge excluded

    o Units closed/New Units

    Waste Stream wise Quantification of Hazardous Wastes

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    Product Waste Stream WGF (kg/tonne of product)

    Ethylene/Propylene Spent caustic from CausticTower

    0.06

    Oil Soaked Carbonaceous Coke 0.017

    Spent Palladium Catalyst 0.007

    Butadiene Butadiene Polymer Waste 0.06

    Solvent regeneration residue 0.4

    Benzene Spent Nickel Catalyst 0.03

    Spent Nickel-MolybdenumCatalyst

    0.003

    Spent Cobalt-MolybdenumCatalyst 0.007

    Waste Stream wise Quantification of Hazardous Wastes

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    Product Waste Stream WGF (kg/tonne of product)

    Xylene Spent clay 0.50

    Vinyl ChlorideMonomer

    Carbon Waste 0.02

    EDC Bottom Viscous 4.0

    Reactor Waste 0.014

    Polyvinyl Chloride PVC Wet resin 4.0

    Ethylene Oxide/Ethylene Glycol

    Spent Silver catalyst 0.08

    Polythylene Polymeric waste 0.02

    Extruder waste 2.4

    Maleic anhydride Distillation bottoms 60

    ETP sludge 0.4

    Waste Stream Contd. ..

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    Product Waste Stream WGF (kg/tonne ofproduct)

    Phthalic Anhydride Vanadium pentoxide catalyst 167

    Purge cut 24

    Tar residue 12

    Dimethyl Terephthalate Crude ester distillation residue 54

    Linear Alkyl Benzene Calcium fluoride sludge 6.0

    Spent alumina 0.32Spent catalyst 0.04

    Spent molecular sieve 0.35

    Spent carbon 0.02

    Oil soaked sand 0.8

    Isopropyl Alcohol Spent copper catalyst 45.0

    Acetone Distillation by product (Tarry waste) 8.0

    Petrochemical Industry : Suggested Waste Recycling Options

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    Product Waste Recycling Measures

    Ethylene/ Propylene Polymeric waste Refining and reuse

    Benzene Spent nickel catalyst Metal recovery

    Spent nickel-molybdenumcatalyst

    Metal recovery

    Spent cobalt-molybdenum

    catalyst

    Metal recovery

    Polyvinyl chloride PVC wet resin Reuse for manufacturinguseful items

    Isopropyl alcohol Spent copper catalyst Recovery of acid

    Acetone/Phenol Solvent waste Use as a fuel in the boiler

    Polypropylene Powder waste Melting, extrusion andconversion to low-gradearticles

    Cumene Cumene catalyst Acid recovery

    Cumene bottoms Use as a fuel

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    HW Generating Industries & HW Generation

    C ti Fi

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    S.No. State No. ofIndustriesas per HWM

    Rules, 1989

    Total HWgeneration inTPA

    HW generatingIndustries(No.s) as per

    HWM Rules,2000/2003

    Total HWgenerationin TPA

    1. AP 501 1,11,098 1532 507046

    2. Assam 18 1,66,008 23 4,000

    3. Bihar 42 26,575 31 Not given

    4. Chandigarh 47 305 271 8,4255. Delhi 403 1,000 1777 17,000

    6 Goa 25 6,598 49 Not Provided

    7. Gujarat 2984 4,30,030 6052 12, 07,000

    8. Haryana 309 31,046 889 14,972

    9. Himachal 116 2159 575 Not given10. Karnataka 454 1,03,243 1589 92,013

    11. Kerala 133 1,54,722 423 83,530

    12. Maharashtra 3953 20, 07,846 4571 14,07,480

    13. MP 183 1,98,669 753 Not given

    14. Orissa 163 3,41,144 257 74,918

    Comparative Figures

    HW Generating Industries & HW Generation

    C ti Fi

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    S.

    No.

    Name of theState

    No. ofIndustries asper HWM

    Rules, 1989

    Total HWgeneration inTPA

    No. of HWIndustries asper HWM

    Rules,2000/2003

    Total HWgenerationin TPA

    16. Pondicherry 15 8,893 66 30,320

    17. Punjab 700 22,709 1448 15,769

    18. Rajasthan 332 1,22,307 512 1,83,737

    19. Tamilnadu 11003,94,208

    2177 1,81, 624

    20. Uttarpradesh 1036 1,45,786 1633 82,375

    21. West Bengal 440 1,29,826 568 Not given

    22 Chattisgarh - - 149 Not given

    23. Mizoram - - Nil Nil

    24. Meghalaya - - 39 37, 41225. Nagaland - - 03 448

    26. Daman, Diu &DNH

    - - 598 Not given

    27. Jharkhand - - 169 Not given

    28. Uttaranchal - - 137 Not given

    29. Manipur - - Nil -

    Comparative Figures

    STATE-WISE COMPARATIVE HW GENERATING UNITS AS

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    PER HWM RULES, 1989 & 2003

    309

    47

    116133

    183 163

    57

    271

    889

    575

    423

    753

    257207

    0

    100

    200

    300

    400

    500

    600

    700

    800

    900

    1000

    Chandigarh

    Haryana

    Hima

    chal

    Ke

    rala

    MP

    Or

    issa

    J

    &K

    STATE

    No.

    ofHWg

    eneratingUn

    its

    HW generating Units as per HWM RULES, 1989

    HW generating Units as per HWM RULES, 2003

    Comparative HW generating Units as

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    501

    1532

    2984

    6052

    454

    1589

    3953

    4571

    700

    1448

    1100

    2177

    1036

    1633

    0

    1000

    2000

    3000

    4000

    5000

    6000

    7000

    AP

    Gujarat

    Karnataka

    Mahara

    shtra

    P

    unjab

    TN

    UP

    State

    perHWM Rules, 1989 and 2003

    No. of HW units as per HWM Rules, 1989

    No. of HW units as per 2003

    HWs - Landfillable, Recyclable,

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    650

    410

    147

    230

    264

    126

    626

    628

    154

    56 109

    0

    200

    400

    600

    800

    1000

    1200

    1400

    1600

    Guja

    rat

    AP

    Ma

    haras

    htr

    Oris

    sa

    State

    Incinerable as per HWM Rules, 2003

    Landfillable Recyclable Incinerable

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    S No State Total HW No of TSDF in No of sites No of sites

    Status on HW Generation & TSDF in Operation in Major States

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    S.No.

    State Total HW

    generation in

    000 TPA

    No. of TSDF inoperation/underconstruction

    No. of sites

    notified

    No. of sites

    identified

    1. AP 507 01 02 02

    2. Assam 4 - - -3. Chandigarh 8 - - -

    4. Delhi 17 Nil Nil 03

    6 Goa - Nil Nil Nil

    7. Gujarat 1207 07 16 22

    8. Haryana 15 - 01 01

    9. Himachal - - 02

    10. Karnataka 92 Nil 02 02

    11. Kerala 84 Nil 01 01

    12. Maharashtra 1407 02 02 06

    13. MP - Nil Nil 03

    14. Orissa 75 Nil 01 0115. Pondicherry 30 Nil Nil Nil

    16. Punjab 16 Nil 01 01

    17. Rajasthan 184 Nil 01 08

    18. Tamilnadu 182 Nil 01 03

    19. Uttarpradesh 82 Nil 03 05

    Common TSDFMulti State

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    Flexibility for Industries located on Inter

    State Border

    Problem facing smaller States/UTs

    Incinerable wasteMin. Scale of operation

    - about 1.0 ton per hour

    Practical Difficulties: Delhi, Chandigarh,

    Daman, Goa

    Incinerable HW as per HWM Rules 2003

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    9.3 12.6

    61.4

    147 154

    02040

    6080

    100120140160180

    Orissa

    AP

    UP

    Gujarat

    Maha

    rashtra

    State

    IncinerableHWin

    '000

    Tonnes

    Incinerable HW as per HWM Rulex, 2003

    Recycling of Hazardous Waste

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    Import of specified categories permitted for Recyclingusing environmentally sound technology

    Recycling of hazardous waste is permitted for unitsregistered with CPCB and having ESM Facilities.

    Guidance Document prepared on ESM of followingRecyclable wastes : Used Oil, Waste Oil, Non-ferrousmetals wastes

    Technology Up gradation: linked to scale of operation

    Large Gap between Demand and Supply w.r.t Lead ,Copper and Zinc wastes.

    India favours free movement of recyclables.

    Recycling of Hazardous Waste contd

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    Recyclable Wastes for which State of Art Facilities areneeded

    Mercury Bearing wastes.

    Nickel Cadmium Batteries

    Spent Catalyst

    E- Waste:

    Guidance document under preparation covering

    i ) Informal sectorii ) leaded glassiii) precious metals recovery etc.,

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